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生物硫酸转化:反应器设计与过程优化。

Biological sulfuric acid transformation: Reactor design and process optimization.

机构信息

Ciba-Geigy AG, WS 2074, 14, CH-4133, Schweizerhalle, Switzerland.

出版信息

Biotechnol Bioeng. 1993 Feb 5;41(3):303-15. doi: 10.1002/bit.260410304.

DOI:10.1002/bit.260410304
PMID:18609554
Abstract

As an alternative to the current disposal technologies for waste sulfuric acid, a new combination of recycling processes was developed. The strong acid (H(2)SO(4)) is biologically converted with the weak acid (CH(3)COOH) into two volatile weak acids (H(2)S, H(2)CO(3)) by sulfate-reducing bacteria. The transformation is possible without prior neutralization of the sulfuric acid. The microbially mediated transformation can be followed by physiochemical processes for the further conversion of the H(2)S.The reduction of sulfate to H(2)S is carried out under carbon-limited conditions at pH 7.5 to 8.5. A fixed-bed biofilm column reactor is used in conjunction with a separate gas-stripping column which was installed in the recycle stream. Sulfate, total sulfide, and the carbon substrate (in most cases acetate) were determined quantitatively. H(2)S and CO(2) are continually removed by stripping with N(2). Optimal removal is achieved under pH conditions which are adjusted to values below the pK(a)-values of the acids. The H(2)S concentration in the stripped gas was 2% to 8% (v/v) if H(2)SO(4) and CH(3)COOH are fed to the recycle stream just before the stripping column.Microbiol conversion rates of 65 g of sulfate reduced per liter of bioreactor volume per day are achieved and bacterial conversion efficiencies for sulfate of more than 95% can be maintained if the concentration of undissociated H(2)S is kept below 40 to 50 mg/L. Porous glass spheres, lava beads, and polyurethane pellets are useful matrices for the attachment of the bacterial biomass. Theoretical aspects and the dependence of the overall conversion performance on selected process parameters are illustrated in the Appendix to this article.

摘要

作为当前废硫酸处理技术的替代方案,开发了一种新的回收工艺组合。强酸性(H(2)SO(4))通过硫酸盐还原菌与弱酸性(CH(3)COOH)生物转化为两种挥发性弱酸性(H(2)S,H(2)CO(3))。硫酸无需预先中和即可进行转化。微生物介导的转化可以通过物理化学过程进一步转化 H(2)S。在 pH 7.5 到 8.5 下,在碳受限条件下将硫酸盐还原为 H(2)S。使用固定床生物膜柱反应器与单独的气体汽提柱结合使用,该汽提柱安装在循环流中。硫酸盐、总硫化物和碳基质(在大多数情况下为乙酸盐)被定量测定。H(2)S 和 CO(2)通过用 N(2)汽提不断去除。在调整至低于酸的 pK(a)值的 pH 条件下,可实现最佳去除效果。如果在进入汽提柱之前将 H(2)SO(4)和 CH(3)COOH 进料到循环流中,则汽提气体中的 H(2)S 浓度为 2%至 8%(v/v)。如果保持未离解的 H(2)S 浓度低于 40 至 50mg/L,则可以实现每升生物反应器体积每天还原 65g 硫酸盐的微生物转化速率,并且硫酸盐的细菌转化率可以保持在 95%以上。多孔玻璃球、熔岩珠和聚氨酯颗粒是附着细菌生物量的有用基质。本文附录中说明了理论方面和整体转化性能对选定工艺参数的依赖性。

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